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Aquaculture governance and controversy in Norway

Jahn Petter Johnsen1, Otto Andreassen2, Bjørn Hersoug12 and Ann-Magnhild Solås12

1Norwegian College of Fishery Science, University of Tromsø – the Arctic University of Norway,

2Nofima, Tromsø, Norway Abstract:

Natural resource governance is based on interventions that regulate human behavior (Berkes, 2007).

The interventions are defined on basis of assumption of how human actions impact on nature (Pálsson 2006). Since nature is not directly accessible, nature has to be represented through specific governable objects that can be the foundation for defining interventions (Johnsen et al. 2009, Johnsen 2014). Governable objects are constituted when the components and processes in an ecosystem through specific techniques are symbolically transformed into bounded objects that can be measured, quantified or modeled in ways that make it possible to create specific intervention mechanisms for governance, as is done with a fish stock. “The managed fish stock” can serve as an example of the creation of a governance object. The fish stock” is produced through modeling and simulation as an object of knowledge that over time will be more and more stable and durable as a governance object. The fish stock that we regulate is in this sense “constructed”.

In our conceptual model (illustrated in slide 14), governance is understood as an interaction between two subsystems: The governing system and the system-to-be-governed (Jentoft 2007). The governance system produces and processes knowledge about the system-to-be-governed, and converts this knowledge into management instruments, i.e. a system of regulatory practices (Johnsen et al. 2009). This conceptual understanding of governance includes policymaking, decision-making, administrative actions and formal management, and the natural and social interactions that constitute the socio-ecological system-to-be-governed. Governance is used here as having a broader meaning for governing, while management denotes the targeted formal actions that are undertaken to regulate the fish farming. Two mechanisms for information feedback are depicted in the model.

On the right hand side, there is a technical and scientific information system for monitoring the effects on the natural system. The left side of the figure in slide 14 depicts the control and regulatory instruments that have been created to regulate human activity in relation to the estimated effects and impacts. Additionally, a governance system can have public information channels that go directly from the system-to-be-governed, or representatives of this system, to the governing system (middle arrow). In this way, the dynamic and complex character of natural and social systems becomes reduced to specific tangible governable objects. In addition, the political and ideological part of the model illustrates that governance is not only a technical process.

Different from the fish stock, coastal space is still in the making as a governance object. Moreover, while the fish stock management is the responsibility of one knowledge authority, the Institute of Marine Research, one Political authority, the Ministry of Trade and Fisheries, and one executive management body, the Fisheries Directorate, aquaculture governance is more complicated. Coastal space is the responsibility of several knowledge bodies, political and administrative authorities.

Coastal space is not yet constructed and stabilized as a defined and bounded governance object. This has implications for the governance of aquaculture. There are overlapping responsibilities, conflicting goals and values. This organization structure has resulted in a complicated planning and management system with a variety of governance tools – all with great ambitions, but involving

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considerable problems of coordinating the different stakeholder interests – and with tensions between the various governance levels. Local concerns may easily be overrun by national priorities and plans, while national goals may be undermined by local foot dragging and protests (Hersoug 2013).

The Aquaculture controversies in Norway is in one way or another related to management and administrative practice, either through actions meant to help, reveal or attempts to deal with the controversy. Policy objectives, management systems and regulations are all complex, and to some extent characterised by a lack of coordination. Tensions occur both vertically between different management levels, and horizontally between sector authorities, or neighbouring municipalities. This makes it challenging for the industry to relate to the management system, and also to integrate the different governance needs. In addition, there are increased pressures in the coastal zone regarding new ways to harvest, use, and protect coastal nature and resources. Global and external interests also play an increasingly larger role in local communities. Thus, the controversies are very complex.

Disputes over aquaculture in Norway often arise when new licenses are announced by the Ministry of Trade, Industry and Fisheries, when fish farms apply for new or larger sites, and when coastal zone planes are prepared by the local communities (in Norway, planning of the near-shore sea space is a task delegated to the municipalities). The controversies are mostly framed and expressed along four axes; 1) access to sea areas, 2) effects on the natural environment, in particular sea lice and escapes, 3) fishing, commercial- and recreational fishing, and 4) community development, the distribution of advantages and disadvantages.

One of the major themes of the controversy seems to be the struggle for and access to sea areas, but there may be reason to question whether there are other conditions that prevails. Aquaculture is a very area-efficient way to produce food. A normal sized aquaculture site today has around the same extent as the infields at old day’s smallholdings. On such a confined area the annual production volume of farmed salmon are more than the total meat production in the agricultural industry in both Troms and Finnmark County. The overall physical area seizure for all sites for salmon farming in Norway is less than 0.5 percent of the sea area within the baseline of Norway. It is thus likely that the controversy currently are more about political tolerance and social acceptance than lack of physical space, and environmental constraints.

Today, the focus is mainly on environmental concerns, which also are reflected in the regulatory regime where the environmental concerns seems to be almost the only thing that can stop applications for new or bigger aquaculture sites. However, it is obvious that also, other aspects should be taken into consideration, but a narrow focus on environmental sustainability tends to lock the aquaculture controversy in Norway to environmental issues, thus, many fundamental issues regarding the salmon farming industry (social and cultural impact, rights, knowledge, and governance, local versus global development etc.) are suppressed.

Research findings indicate that the controversies might also stem form an immature governance regime that is fragmented, and suffers from a lack of coordination and a diversity of objectives, signals, practices etc. Hence, developing more knowledge about how and why the controversies arise is essential. So is developing governance models that reduces and resolves controversies, rather than adding to them.

84 References:

Berkes, F. (2007). Sacred ecology, 2nd edition. Routledge. New York and London: Taylor and Francis Group.

Hersoug, B. (2013). The battle for space: The position of Norwegian aquaculture in integrated coastal zone planning. In: Global challenges in integrated coastal zone management (Eds. Moksness, Dahl & Støttrup). Sussex: Wiley-Blackwell, pp. 159–168.

Jentoft, S. (2007). Limits of governability: Institutional implications for fisheries and coastal governance. Marine Policy, 31, pp. 360–370.

Johnsen, J.P. (2014). Is fisheries governance possible? Fish and Fisheries, 15:3, pp. 428–444.

Johnsen, J.P., P. Holm, S. Sinclair & D. Bavington (2009). The cyborgisation of the fisheries. On attempts to make fisheries management possible. Maritime Studies (MAST),7, pp. 9–34.

Pálsson, G. (2006). Nature and society in the age of post-modernity. In: Reimagining political ecology (Eds. A. Biersack and J.B. Greenberg). Durham, NC: Duke University Press, pp. 70–93.

Links to two articles about space as governance object:

http://www.maritimestudiesjournal.com/content/13/1/2 http://www.ecologyandsociety.org/vol19/iss2/art60/

 

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Aquaculture governance and controversy in Norway   

by   

Jahn Petter Johnsen  Otto Andreassen 

Bjørn Hersoug  Ann‐Magnhild Solås 

Nofima/The Arctic University of Norway   

 

Aquaculture governance DQGFRQWURYHUV\

LQ Norway

Jahn Petter Johnsen, Otto Andreassen, Bjørn Hersoug and  Ann‐Magnhild Solås

EŽĨŝŵĂͬdŚĞƌĐƚŝĐhŶŝǀĞƌƐŝƚLJŽĨEŽƌǁĂLJ

How to govern Nature? 

• Through regulation of human behaviour

• By the use of representations of Nature that  makes interventions possible – Management  Objects

• Due to path dependency and institutional 

“lock‐in” Management Objects will over time  be more and more stable and durable 

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Construction of a Management Object

«The managed fish stock»

• Not the same as the fish in the sea

• Science produces “the fish stock” as an object  of knowledge, through modelling and 

simulation

• Stock estimates are starting point for a bundle  of institutionalised management practices 

• The fish stock is “made” and stable

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D

Different from the fish stock, coastal space

 as a Management   Object is still in making

Theoretical Perspective: 

• Science and Technology study perspective 

• Actor‐Network Theory 

• Management Objects are seen as multiple objects

• Example: Arteriosclerosis. From  Mol A 2002. The  Body Multiple: Ontology in Medical Practice. 

• The cyborg fish, Johnsen, Holm, Sinclair and 

Bavington (2009), Johnsen, Murray and Neis (2009). 

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Norwegian Coastal Planning

The Plan and Building Act  (PBA)(1965)

Municipal responsibility 

Physical planning on land – coordination between sectors  and use of area

Avoid conflicts between different users

1985 – Harbour areas included in the PBA

1989 – Coastal Planning to the baseline

2009 (New PBA) Municipality planning to 1 nm outside the  baseline

Why coastal planning? 

Cages in the sea made it posible to intensify the production

Access to coastal area became an asset and resource for fish farming A struggle for access to area started

The management regime was established

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Ecosystem based approch (EA) 

• Shift in approach and focus from users’ rights  and interests to user impact on the ecosystem

• Rights, impacts and responsibility are seen in  relation

• EA focuses on functionality and dynamics

• Relationships between a variety of actors and  components

• From 2D(area) to 3D (space)

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Anchoring and user conflicts

Physical Chemical

Biological Ecological

Economic Social From area to space : Example: The site for

aquaculture

Interests and stakeholders:

fishers and sea transport

1970s Today

Stakeholders: Many

Cultural Political

Impacts and risks

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Sailing lane

Industry Fishery harbour

Natural and cultural heritage Homes Road brigde view point and social meeting place

Power lines

Functions and impacts

Seagull nesting place

Fisheries Social

system

Natural system M. of Trade,

Industry and Fisheries Directorate of Fisheries

Institute of Marine Research ICES

Licences Catch quotas

Governing system

System to be governed

Governance model: Fisheries

Governance model: Aquaculture

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Governance in Norway:  Aquaculture 

Aquaculture Site Application Process

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Controversy increases when: 

Tromsø havpadleklubb

Forsvarets mediesenter

• New licenses are announced

• Fish farmers apply for new sites

• When coastal zone plans are prepared

Foto: Otto Andreassen

Controversy: A battle for space?

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21 Foto: Otto Andreassen

Controversy: A battle for space, or ..?

Tromsø havpadleklubb

Forsvarets mediesenter

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Controversy in Norway:

• Environmental impact

– Sea lice – Escaping

• Fishing

– Wild salmon  – Marine fish

• Rural  development

– Distribution of advantages and  disadvantages

– Rights

Controversy in Norway;       

mainly focus on environmental issues

• A too narrow focus  and regulation on almost only  environmental issues leads to lock the controversy

• Thus, it leads to hide many fundamental issues  regarding the salmon farming industry (social and  cultural impact, rights, knowledge, and governance,  local versus global development…).

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Does the regulatory regime add to the  controversy?

• Fragmented

• Diversity of objectives  and signals

• Diversity of practises

• Lack of coordination

Increase the production ten times!

Halve the production!

Institute of Marine Research

Directorate of Nature Management

Takk for oss

www.nofima.no

http://www.raesidecartoon.com

Thank you

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